Could Colorado See the Return of Grizzlies, Wolves and Wild Bison? Here’S How Montanans Coexist with Them
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After Long-Term Decline, Are Aspen Recovering in Northern Yellowstone? ⇑ Luke E
Forest Ecology and Management 329 (2014) 108–117 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco After long-term decline, are aspen recovering in northern Yellowstone? ⇑ Luke E. Painter a, , Robert L. Beschta a, Eric J. Larsen b, William J. Ripple a a Department of Forest Ecosystems and Society, Oregon State University, Corvallis, OR 97331, USA b Department of Geography and Geology, University of Wisconsin – Stevens Point, Stevens Point, WI 54481-3897, USA article info abstract Article history: In northern Yellowstone National Park, quaking aspen (Populus tremuloides) stands were dying out in the Received 18 December 2013 late 20th century following decades of intensive browsing by Rocky Mountain elk (Cervus elaphus). In Received in revised form 28 May 2014 1995–1996 gray wolves (Canis lupus) were reintroduced, joining bears (Ursus spp.) and cougars (Puma Accepted 30 May 2014 concolor) to complete the guild of large carnivores that prey on elk. This was followed by a marked decline in elk density and change in elk distribution during the years 1997–2012, due in part to increased pre- dation. We hypothesized that these changes would result in less browsing and an increase in height of Keywords: young aspen. In 2012, we sampled 87 randomly selected stands in northern Yellowstone, and compared Wolves our data to baseline measurements from 1997 and 1998. Browsing rates (the percentage of leaders Elk Browsing effects browsed annually) in 1997–1998 were consistently high, averaging 88%, and only 1% of young aspen Trophic cascade in sample plots were taller than 100 cm; none were taller than 200 cm. -
Wolf Interactions with Non-Prey
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln USGS Northern Prairie Wildlife Research Center US Geological Survey 2003 Wolf Interactions with Non-prey Warren B. Ballard Texas Tech University Ludwig N. Carbyn Canadian Wildlife Service Douglas W. Smith US Park Service Follow this and additional works at: https://digitalcommons.unl.edu/usgsnpwrc Part of the Animal Sciences Commons, Behavior and Ethology Commons, Biodiversity Commons, Environmental Policy Commons, Recreation, Parks and Tourism Administration Commons, and the Terrestrial and Aquatic Ecology Commons Ballard, Warren B.; Carbyn, Ludwig N.; and Smith, Douglas W., "Wolf Interactions with Non-prey" (2003). USGS Northern Prairie Wildlife Research Center. 325. https://digitalcommons.unl.edu/usgsnpwrc/325 This Article is brought to you for free and open access by the US Geological Survey at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in USGS Northern Prairie Wildlife Research Center by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. 10 Wolf Interactions with Non-prey Warren B. Ballard, Ludwig N. Carbyn, and Douglas W. Smith WOLVES SHARE THEIR ENVIRONMENT with many an wolves and non-prey species. The inherent genetic, be imals besides those that they prey on, and the nature of havioral, and morphological flexibility of wolves has the interactions between wolves and these other crea allowed them to adapt to a wide range of habitats and tures varies considerably. Some of these sympatric ani environmental conditions in Europe, Asia, and North mals are fellow canids such as foxes, coyotes, and jackals. America. Therefore, the role of wolves varies consider Others are large carnivores such as bears and cougars. -
Effects of Wolf Reintroduction on Coyote Temporal Activity
Background Information and Study Design: Motivation: Effects of Wolf We will conduct an observational study in Montana, Wisconsin, and Maine, which are spread out over the U.S. - In each of these states we will have ● After wolves (Canis lupus) were driven to extinction in Reintroduction three control groups and three experimental groups where we study the the United States, coyotes (Canis latrans) expanded temporal activity of both wolves and coyotes. into niches previously occupied by wolves. on Coyote As a control group, we will study areas where coyotes live, but wolves have ● 1990’s - efforts were made to reintroduce wolves; led yet to be reintroduced. to successful re-establishment of several wolf packs Temporal Activity We plan on monitoring temporal activity through the use of radio collars to and a return to their status as the dominant predator By Tessa Garufi, Lily Grady, and track coyote movement. If movement is occurring primarily at night with no ● In areas where wolves and coyotes now coexist, Libby Boulanger motion during the day, it can be reasoned that the coyotes in the area are coyotes experience increased pressure - they have to primarily nocturnal and if movement is during the day with no motion at night, contend with the risk of wolf-caused mortalities and it can be reasoned that they are primarily diurnal. Wolf temporal activity will resource competition against a more dominant also be monitored to determine how different the activity timing of wolves and predator. coyotes are in areas where they coexist. ● We want to determine if coyotes living in the same area as wolves have experienced a temporal niche Intended Analysis shift as a response to the increased pressure - if a Because our independent variable is categorical with two groups shift has occurred, it could lead to an increase in (wolves present or wolves absent) and our response variable is potentially harmful coyote-human interactions. -
Red Wolf Brochure
U.S. Fish & Wildlife Service Endangered Red Wolves The U.S. Fish and Wildlife Service is reintroducing red wolves to prevent extinction of the species and to restore the ecosystems in which red wolves once occurred, as mandated by the Endangered Species Act of 1973. According to the Act, endangered and threatened species are of aesthetic, ecological, educational, historical, recreational, and scientific value to the nation and its people. On the Edge of Extinction The red wolf historically roamed as a top predator throughout the southeastern U.S. but today is one of the most endangered animals in the world. Aggressive predator control programs and clearing of forested habitat combined to cause impacts that brought the red wolf to the brink of extinction. By 1970, the entire population of red wolves was believed to be fewer than 100 animals confined to a small area of coastal Texas and Louisiana. In 1980, the red wolf was officially declared extinct in the wild, while only a small number of red wolves remained in captivity. During the 1970’s, the U.S. Fish and Wildlife Service established criteria which helped distinguish the red wolf species from other canids. From 1974 to 1980, the Service applied these criteria to find that only 17 red wolves were still living. Based on additional Greg Koch breeding studies, only 14 of these wolves were selected as founders to begin the red wolf captive breeding population. The captive breeding program is coordinated for the Service by the Point Defiance Zoo & Aquarium in Tacoma, Washington, with goals of conserving red wolf genetic diversity and providing red wolves for restoration to the wild. -
Grizzly Bear Fact Sheet
Identify Grizzly from Black Bears Grizzly bears typically weigh 100-200 kg (females) to 200-300 kg (males) which is slightly more than black bears. Grizzly bears have a shoulder hump, range in colour from blonde to black and may have silver or light- tipped guard hairs on their head, hump and back. A grizzly bear’s ears are rounded and appear smaller than the black bear, while the black bear has more pointed, noticeable ears and no shoulder hump. Grizzly bear claws are longer than those of black bears and may have a light-coloured stripe. In grizzly bear ISBN: 978-0-7785-8683-8 (Printed Version) tracks, the tips of the front claws usu- 978-0-7785-8683-8 (Online Version) ally leave imprints in front of the paw Printed July 2009 pad, and the toes are set in a nearly straight line. In black bear tracks, the claw imprints are difficult to see, and the front toes form an obvious arc. Reproduction Range Grizzly bear numbers are limited by a slow reproductive rate. This is Grizzly bears can be found caused by a relatively high age of first reproduction, small litter siz- in Alberta from the Montana es, and long periods between litters. In Alberta, most female grizzlies border, along the mountains do not have their first litter until they are at least four years old and and foothills and continuing usually have only one or two cubs. The cubs are born in January or north through the western February and stay with their mother for two to five years. -
How People Should Respond When Encountering a Large Carnivore: Opinions of Wildlife Professionals Dy L a N E
Human–Wildlife Conflicts 2(2):194–199, Fall 2008 How people should respond when encountering a large carnivore: opinions of wildlife professionals DYLA N E. BRO wn , 507 Silo Loop, Kinsey, Montana 59338, USA [email protected] MI C HAEL R. CO N OVER , Jack H. Berryman Institute, Department of Wildland Resources, Utah State University, Logan, Utah 84322-5230, USA Abstract: We conducted telephone surveys of wildlife professionals who work with large carnivores to ask their opinions about how people should respond to avoid being injured when confronted by a black bear (Ursus americana), grizzly bear (Ursus arctos), mountain lion (Puma concolor), or gray wolf (Canis lupus). The respondents agreed that the most appropriate response was to try to increase the distance between a person and the carnivore. In the event of an attack by a black bear, mountain lion, or wolf, most respondents said to fight back. Opinion was divided over the best response for an individual who was being attacked by a grizzly bear, but a slight majority of professionals said to fight back if the attack was predatory and be passive if the attack was defensive; however, respondents also noted that many victims would be unable to identify the bear’s motive. If a black bear came into camp, most respondents said that a person should aggressively encourage the bear to leave and to fight back against a bear that enters a tent at night, regardless of species. Respondents unanimously agreed that bear pepper-spray is effective in defending against an attack. While any encounter with a large carnivore can be fatal to the person involved, we believe that selecting the right course of action increases the odds that the victim can escape without injury. -
Predation by a Golden Eagle on a Brown Bear Cub
SHORT COMMUNICATION N Sørensen et al. Predation by a golden eagle on a brown bear cub Ole J. Sørensen1,4, Mogens Totsa˚ s2, Tore eagles attending bears. Murie hypothesized that Solstad2, and Robin Rigg3 eagles attending bears were waiting for opportunities to capture prey trying to escape from the bears. He 1North-Trondelag University College, Department of also observed eagles swooping at and diving low over Natural Resource Sciences and Information Technology, grizzlies and other carnivores, but interpreted this Box 2501, N-7729 Steinkjer, Norway behavior as play or curiosity, rather than predation. 2 Norwegian Nature Inspectorate, N-7485 Trondheim, C. McIntyre (US National Park Service, Fair- Norway 3 banks, Alaska, USA, personal communication, 2008), Slovak Wildlife Society, PO Box 72, 033 01 Liptovsky a golden eagle researcher in Denali National Park for Hradok, Slovakia many years, has never seen an eagle attack a bear, although she has often observed eagles following Abstract: During spring 2004 an adult female brown bears in open terrain, perhaps positioning themselves bear (Ursus arctos) and her 3 cubs-of-the-year were to take prey escaping from the bear as suggested by observed outside their den on a south-facing low- Murie. Commensalistic hunting, as well as curious or alpine slope in central Norway. They remained near play behavior by eagles in the vicinity of bears, could the den for 8–10 days and were, except for one day, be misinterpreted as eagles hunting, attacking, or observed daily by Totsa˚s and other wardens of the inspecting bears as possible prey. Predation by eagles Norwegian Nature Inspectorate. -
The Effects of the Lake Trout Introduction in Yellowstone Lake on Populations Outside the Aquatic a Meta-Analytic Study
Migrate, Mutate, or Die: The effects of the lake trout introduction in Yellowstone Lake on populations outside the aquatic A Meta-Analytic Study By Sarah Z. Gandhi-Besbes University of Colorado at Boulder A thesis submitted to the University of Colorado at Boulder in partial fulfilment of the requirements to receive Honours designation in Environmental Studies May 2016 Thesis Advisors: Alexander Cruz, Ecology and Evolutionary Biology, Committee Chair Dale Miller, Environmental Studies Andrew Martin, Ecology and Evolutionary Biology © 2016 by Sarah Z. Gandhi-Besbes All rights reserved i Abstract Yellowstone National Park is a relatively pristine ecosystem preserved through time. The Yellowstone cutthroat trout Oncorhynchus clarkii bouvieri population, inhabiting shallower waters in Yellowstone Lake and spawning in its tributaries, has been declining primarily due to the introduction of a predatory fish. The lake trout Salvelinus namaycush, which rapidly grow to large sizes, feed on the Yellowstone cutthroat trout, breed and spawn in Yellowstone Lake, and dwell in deeper waters out of predatory reach. The Yellowstone cutthroat trout is relied upon both directly and indirectly by more than 40 species within Yellowstone National Park. The grizzly bear Ursus arctos horribilis, bald eagle Haliaeetus leucocephalus, and osprey Pandion halaetus all feed directly on the spawning fish. This study looks at how the declining Yellowstone cutthroat trout populations affect these predatory populations, and what their populations may look like should current trends continue into the year 2030. Conducting a meta-analysis and collecting primary data allowed for statistical projections predicting and comparing estimated future populations. The ecological change in Yellowstone Lake provides insight into how the concerns of one ecosystem affects multiple. -
Wyoming Gray Wolf Monitoring and Management 2019 Annual Report
WYOMING GRAY WOLF MONITORING AND MANAGEMENT 2019 ANNUAL REPORT Prepared by the Wyoming Game and Fish Department in cooperation with the National Park Service, U.S. Fish and Wildlife Service, USDA-APHIS-Wildlife Services, and Eastern Shoshone and Northern Arapahoe Tribal Fish and Game Department to fulfill the U.S. Fish and Wildlife Service requirement to report the status, distribution and management of the gray wolf population in Wyoming from January 1, 2019 through December 31, 2019. EXECUTIVE SUMMARY At the end of 2019, the wolf population in Wyoming remained above minimum delisting criteria; making 2019 the 18th consecutive year Wyoming has exceeded the numerical, distributional, and temporal delisting criteria established by the U.S. Fish and Wildlife Service. At least 311 wolves in ≥43 packs (including ≥22 breeding pairs) inhabited Wyoming on December 31, 2019. Of the total, there were ≥94 wolves and ≥8 packs (≥7 breeding pairs) in Yellowstone National Park, ≥16 wolves and ≥3 packs (1 breeding pair) in the Wind River Reservation, and ≥201 wolves and ≥32 packs (≥14 breeding pairs) in Wyoming outside Yellowstone National Park and the Wind River Reservation (WYO). In WYO, ≥175 wolves in ≥27 packs resided primarily in the Wolf Trophy Game Management Area where wolves are actively monitored and managed by the Wyoming Game and Fish Department and ≥26 wolves in ≥5 packs in areas where wolves are designated primarily as predatory animals and are not actively monitored. A total of 96 wolf mortalities were documented statewide in Wyoming in 2019: 92 in WYO, 3 in Yellowstone National Park, and 1 in the Wind River Reservation. -
Yellowstone Grizzly Bears: Ecology and Conservation of an Icon of Wildness
YELLOWSTONE GRIZZLY BEARS ecology and conservation of an ICON OF WILDNESS EDITED BY P.J. White, Kerry A. Gunther, and Frank T. van Manen YELLOWSTONE GRIZZLY BEARS Yellowstone Grizzly Bears: Ecology and Conservation of an Icon of Wildness Editors P. J. White, Kerry A. Gunther, and Frank T. van Manen Contributing Authors Daniel D. Bjornlie, Amanda M. Bramblett, Steven L. Cain, Tyler H. Coleman, Jennifer K. Fortin-Noreus, Kevin L. Frey, Mark A. Haroldson, Pauline L. Kamath, Eric G. Reinertson, Charles T. Robbins, Daniel J. Thompson, Daniel B. Tyers, Katharine R. Wilmot, and Travis C. Wyman Managing Editor Jennifer A. Jerrett YELLOWSTONE FOREVER, YELLOWSTONE NATIONAL PARK AND U.S. GEOLOGICAL SURVEY, NORTHERN ROCKY MOUNTAIN SCIENCE CENTER Yellowstone Forever, Yellowstone National Park 82190 Published 2017 Contents Printed in the United States of America All chapters are prepared solely by officers or employees of the United States Preface ix government as part of their official duties and are not subject to copyright protection Daniel N. Wenk, Superintendent, Yellowstone National Park in the United States. Foreign copyrights may apply. National Park Service (NPS) photographs are not subject to copyright protection in the United States. Foreign Introduction xv copyrights may apply. However, because this work may contain other copyrighted images or other incorporated material, permission from the copyright holder may be P. J. White, Kerry A. Gunther, and Frank T. van Manen necessary. Cover and half title images: www.revealedinnature.com by Jake Davis. Chapter 1: The Population 1 Library of Congress Cataloging-in-Publication Data P. J. White, Kerry A. Gunther, and Travis C. -
47 C. OTHER FEDERALLY LISTED SPECIES WITHIN the RANGE SPOTTED OWL 47 Oregon Silverspot Butterfly 47 Aleutian Canada Goose 48
47 C. OTHER FEDERALLY LISTED SPECIES WITHIN THE RANGE SPOTTED OWL 47 Oregon Silverspot Butterfly 47 Aleutian Canada Goose 48 Bald Eagle 49 Peregrine Falcon 50 Gray Wolf 50 Grizzly Bear 51 Columbian White-tailed Deer C. Other Fe Range of the No Nine wildlife species within the range of the northern spotted owl are listed by the federal government as threatened or endangered: the northern spotted owl, marbled murrelet, Oregon silverspot butterfly, Aleutian Canada goose, bald eagle, peregrine falcon, gray wolf, grizzly bear, and Columbian white-tailed deer. Discussions of species ecology for the spotted owl and marbled murrelet are found in Sections A and B of this chapter, respectively. Habitat needs of the other seven species are reviewed below, followed by Table 111.8, which lists for each of the nine species its federal and state status and in which HCP planning unit each could potentially occur. on Silvers The Oregon silverspot butterfly (Speyeria zerene hippolyta) is the only federally listed species of arthropod that is found in Washington (WDW 1993a). This butterfly is currently listed by the federal government as threatened and by the state as endangered. However, no critical habitat in I Washington has been designated under the Endangered Species Act (WDW 1993b). The Oregon silverspot is found only in habitats that support its larval host plant, western blue violet (Viola adunca). Such habitats include coastal salt-spray meadows and open fields. In Washington, potential habitat for the Oregon silverspot is limited to the coastal grasslands on the Long Beach peninsula near Loomis Lake (WDW 199313; WDW 1991).Adult butterflies are thought to rest and feed in adjacent open spruce/shoreline pine forest glades, where they are protected from wind and can feed on nectar available from a number of plant species. -
Yellowstone Wolf Project: Annual Report, 1997
Suggested citation: Smith, D.W. 1998. Yellowstone Wolf Project: Annual Report, 1997. National Park Service, Yellowstone Center for Resources, Yellowstone National Park, Wyoming, YCR-NR- 98-2. Yellowstone Wolf Project Annual Report 1997 Douglas W. Smith National Park Service Yellowstone Center for Resources Yellowstone National Park, Wyoming YCR-NR-98-2 BACKGROUND Although wolf packs once roamed from the Arctic tundra to Mexico, they were regarded as danger- ous predators, and gradual loss of habitat and deliberate extermination programs led to their demise throughout most of the United States. By 1926 when the National Park Service (NPS) ended its predator control efforts, Yellowstone had no wolf packs left. In the decades that followed, the importance of the wolf as part of a naturally functioning ecosystem came to be better understood, and the gray wolf (Canis lupus) was eventually listed as an endangered species in all of its traditional range except Alaska. NPS policy calls for restoring native species that have been eliminated as a result of human activity if adequate habitat exists to support them and the species can be managed so as not to pose a serious threat to people or property outside the park. Because of its size and the abundant prey that existed here, Yellowstone was an obvious choice as a place where wolf restoration would have a good chance of succeeding. The designated recovery area includes the entire Greater Yellowstone Area. The goal of the wolf restoration program is to maintain at least 10 breeding wolf pairs in Greater Yellowstone as it is for the other two recovery areas in central Idaho and northwestern Montana.